Zhiqiang Pang*ab,
Jiachuan Chena,
Cuihua Donga and
Guihua Yanga
aKey Laboratory of Pulp and Paper Science and Technology of Ministry of Education, Qilu University of Technology, Jinan, Shandong Province 250353, China. E-mail: zpang5@wisc.edu
bJiangsu Provincial Key Laboratory of Pulp and Paper Science and Technology, Nanjing Forestry University, Nanjing, Jiangsu Province 210037, China
First published on 24th June 2014
Aqueous ionic liquids (ILs) that selectively extract lignin in kraft pulp under benign conditions were reported. This study provided an innovative idea to isolate the three-dimensional lignin from a recalcitrant matrix with the benefits of decreased dosage of bleaching chemicals, degradation of cellulose and toxicity of bleaching effluent.
Ionic liquids (ILs) have been receiving much attention because of their unique properties such as nearly total non-volatility, high oxidative and thermal stabilities, wide liquid temperature range, and tunable properties.7,8 Efficient and environmentally friendly processing of lignocelluloses is gradually feasible when ILs are used as green solvent for its particular ability on breaking hydrogen bond networks.9 The structure and reactivity of cellulose largely depend on the quantity and intensity of hydrogen bonds. Accordingly, cellulose is divided into crystalline and amorphous zones on the basis of glucose arrangement. The macromolecular matrix of lignin and hemicellulose also has extensive hydrogen bonds. Cellulose dissolution by ILs has been thoroughly investigated. However, the effect of ILs on lignin is still not fully understood. Many imidazolium-based ILs were demonstrated to be good solvent for lignin which contain methyl, ethyl, allyl, butyl, hexyl and benzyl groups in the imidazolium ring and chloride, bromide, tetrafluoroborate, acetate and methylsufate as anions, especially the large non-coordinating anions were not favourable of lignin dissolution.10–12 Complete dissolution of lignocellulose requiring harsh conditions, such as Norway spruce sawdust dissolved in 1-allyl-3-methylimidazolium chloride (AmimCl) at 110 °C for 8 h with a solubility of 8 wt%, has been widely accepted.13 Particle size and water content are the two crucial parameters that define solubilization.14 We showed in our previous study that mild treatment of pulps by ILs resulted in fiber swelling and decreased cohesive force.15 The dissolution of cellulose by ILs was not necessary in pulp processing and was only a requirement for lignin removal. Several studies have examined the complete dissolution of lignocellulose by ILs. Developing an easy-to-make and cost-effective processing of lignocellulose by ILs would be highly welcomed. Although the application of ILs is still seriously hindered by cost, processing, and recycling,16 elucidating the extraction mechanism by aqueous ILs would provide a powerful basis for an efficient novel molecular design and the isolation of a three-dimensional macromolecule.
In this paper, we present an innovative method of lignin extraction in lignocellulose for green bleaching of kraft pulp involving pretreatment with aqueous ILs under benign conditions. Deconstruction of compact woody lignocellulose using ILs is difficult. Small particle-sized sample facilitates the diffusion of ILs, but the communition of lignocellulose to small size consumes a considerable amount of energy. Kraft pulp is obtained by cooking with nearly 50 wt% loss of feedstock. Thus, woody lignocellulose separates into pulp with a loose structure, which results in the diffusion of ILs. Correspondingly, the energy-consuming communition can be cancelled. The presence of water induces competitiveness between the hydrogen bonds of pulp with ILs, and the dissolving efficiency decreases markedly with water content. However, both ILs and lignocellulose naturally exhibit strong hydroscopicity and apt to absorb water from atmosphere. Dehydration is also extremely cost consuming, especially at low water content. Additionally, water itself is a solvent in paper making, and only the removal of lignin is expected without fiber dissolution in bleaching. Hence, kraft pulp is the ideal object for treatment by benign ILs and chosen as the lignocellulosic material in our study. We designed a process incorporating IL pretreatment under benign conditions with water to extract residual lignin with negligible degradation on cellulose for enhanced bleaching properties.
The performance of ILs was significantly affected by water molecules.17 The presence of water in ILs decreased the solubility of cellulose. When water was added to IL at concentrations greater than ca. 1.0 wt% (approximately 0.5 mole fraction H2O), the solvent properties of ILs were remarkably impaired, leaving cellulose insoluble. Kraft pulps were treated with 1-butyl-3-methylimidazolium chloride (BmimCl) or AmimCl (at 70 °C with IL dosage of 3.0 mL g−1 pulp for 30 min) with varying water content. The intensity of the treatment was considerably weaker than that of the dissolution of lignocellulose by ILs, for example, lignin fractionation with 97 wt% purity from wheat straw requires complete dissolution of biomass by 1-ethyl-3-methylimidazolium acetate ([emim][CH3COO]) pretreatment with biomass/IL ration of 5% (w/w) at 140 °C for 6 h.18,19 Table 1 shows that residual lignin in pulp can be substantially extracted by BmimCl pretreatment when the water content was below 12.0 wt%. The percentage of lignin extraction exceeded 20.0 wt% when the water content was below 3.0 wt%. Aside from cellulose dissolution, water content also remarkably influenced lignin extraction. Lignin extraction of aqueous IL solutions decreased sharply with increased water content, and almost no lignin was extracted when the water content was higher than 12.0 wt%. AmimCl pretreatment was performed similar to BmimCl pretreatment (Table S1†).
Water content, % | Lignin content, % | Viscosity, mL g−1 | Brightness, %ISO | Yield, % | COD, mg g−1 pulp | BOD, mg g−1 pulp | AOX, mg g−1 pulp |
---|---|---|---|---|---|---|---|
0 | 2.24 | 765.1 | 83.1 | 86.3 | 65.1 | 14.4 | 0.36 |
3 | 2.33 | 767.5 | 82.7 | 86.6 | 65.8 | 14.5 | 0.39 |
6 | 2.48 | 769.2 | 81.8 | 86.8 | 66.4 | 14.6 | 0.42 |
9 | 2.64 | 771.8 | 80.6 | 87.0 | 67.0 | 14.6 | 0.45 |
12 | 2.69 | 773.2 | 79.2 | 87.1 | 67.5 | 14.7 | 0.48 |
15 | 2.99 | 775.4 | 78.4 | 87.2 | 68.1 | 14.8 | 0.52 |
Control sample | |||||||
3.00 | 775.6 | 78.3 | 87.2 | 68.2 | 14.8 | 0.53 |
Despite the high degree of lignin extraction, the loss in viscosity of fiber was low; thereby the natural strength of cellulose was maintained. The pretreated pulp was thoroughly washed with water and bleached with chlorine dioxide–chelation–hydrogen peroxide (DQP) bleaching sequence. Compared with the control sample, the brightness of the bleached pulps increased with the degree of lignin extraction in IL pretreatment. Slight loss in viscosity occurred under identical conditions in the bleaching process. At 3 wt% water content, the brightness after DQP bleaching increased to 4.4%ISO, with a reduction in viscosity of only 8.1 mL g−1. The pretreated pulp was subsequently bleached with decreasing dosage of bleaching chemicals. The chemical dosage of DQP bleaching could be decreased to as high as 25.0 wt% at the identical target of brightness with the control samples. Correspondingly, the viscosity increased to ca. 25.0 mL g−1 (Table S2†). The reduction in the degradation degree of cellulose increased the yield of bleaching. Reduced dosage of bleaching chemicals resulted in lower load of pollution effluent, and pre-extraction of lignin decreased adsorbable organic halide (AOX) emission. Less lignin-derived pollutants that resulted in poor reactivity facilitated the effluent treatment.
The structural changes in pulp and lignin were analysed to reveal the mechanism of lignin extraction. The pulps were treated with 3.0 wt% water content (IL dosage of 3.0 mL g−1 pulp at 70 °C for 30 min). Given that no dissolution of cellulose occurred, the macrostructure of pulp was virtually untransformed by aqueous IL treatment and therefore could be used for paper making. The XRD pattern of cellulose was slightly changed by aqueous IL pretreatment (Fig. S1†). The crystallization index (CI) after BmimCl and AmimCl pretreatments was 66.2% and 67.5%, respectively. These values were slightly lower than those of the control sample (CI = 69.1%), which indicates that aqueous ILs mainly act on the amorphous zone of cellulose. The weak action on cellulose only resulted in a negligible loss in viscosity. However, the width of pulp increased from 19.34 μm to 20.12 μm and 19.40 μm for BmimCl and AmimCl pretreatments, respectively. The cellulose was significantly swollen after pretreatment with aqueous ILs under mild conditions. Larger volume of fiber led to a loose and porous structure, which facilitated the diffusion of lignin outside the fibers. Meanwhile, the diffusion of chemicals and degradation products in the subsequent bleaching stages was improved. Regarding the three-dimensional macromolecule of lignin, loosen structure of pulp can improve mass transfer performance favoring lignin extraction. The specific surface area of pulp increased from 2.14 m2 g−1 to 2.36 m2 g−1 (BmimCl pretreatment) and 2.34 m2 g−1 (AmimCl pretreatment). Consequently, the reaction accessibility of pulp increased, which could be attributed to high bleaching efficiency.
Lignin, cellulose, and hemicellulose are the main components of the cell wall of lignocellulose. The effect of ILs on the hydrogen bonds in cellulose was comprehensively evaluated; this effect was believed to be the key factor in cellulose dissolution. However, hydrogen bonds also extensively existed in lignin and hemicellulose. A network of hydrogen bonds was formed in the lignin matrix and its neighboring hemicellulose, contributing a large portion of intermolecular forces of lignin. Under mild conditions, the breakdown of hydrogen bonds in cellulose mainly occurred in the amorphous zone, with a slight decrease in the degree of crystallinity. Thus, the degradation or even the loss of cellulose was avoided, which allowed the retention of the strength and yield of bleached pulp. Although a nonsignificant change with cellulose occurred, the lignin content in pulp after pretreatment decreased substantially. The hydrogen bonds (3000 cm−1 to 3600 cm−1) in polymer was evaluated by IR.20 The area of hydrogen bonds after aqueous IL pretreatment decreased to 17.53% (BmimCl pretreatment) and 15.89% (AmimCl pretreatment), whereas the other functional groups in pulp were nearly unchanged (Fig. 1). Breaking down the hydrogen bonds in lignin structure by aqueous IL pretreatment reduced the intermolecular forces.
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Fig. 1 IR spectra of pulps before and after IL treatment, (A) control sample, (B) sample after BmimCl treatment, and (C) sample after AmimCl treatment. |
The hydroxyl groups in lignin, including aliphatic hydroxyl, phenolic hydroxyl, and carboxyl, substantially decreased after aqueous IL pretreatment (Table 2). The lignin units with more hydroxyls were easily dissolved for the disruption of hydrogen bonds.
Groups | Control | BmimCl | AmimCl |
---|---|---|---|
Aliphatic hydroxyl | 2.18 | 1.95 | 1.92 |
Condensed phenolic hydroxyl | 0.63 | 0.54 | 0.52 |
Syringyl hydroxyl | 0.52 | 0.47 | 0.46 |
Guaiacyl and demethylated hydroxyl | 0.45 | 0.39 | 0.38 |
p-Hydroxy-phenyl hydroxyl | 0.13 | 0.11 | 0.10 |
Total phenolic hydroxyl | 1.73 | 1.50 | 1.46 |
Carboxyl | 0.16 | 0.13 | 0.13 |
The molecular weight distribution and the polydispersity of lignin in pulps before and after aqueous IL treatment were analyzed by gel permeation chromatography (Table 3). The number-average and weight-average molecular weights of lignin increased after aqueous IL pretreatment, whereas the polydispersity decreased. The extracted lignin had a small molecular weight. High-molecular weight lignin was still difficult to dissolve. Low-molecular weight lignin had weak intermolecular forces, and its diffusion ability was strong and easy to dissolve from pulp. This type of lignin also had low condensation degree with higher reactivity and readily reacted with bleaching chemicals in the subsequent bleaching stage and produced pollutants with higher toxicity. Therefore, pre-extraction of lignin by aqueous IL pretreatment could alleviate the toxicity of effluent in the following bleaching stage.
Pulp | Mn | Mw | Polydispersity (Mw/Mn) |
---|---|---|---|
Control | 3215 | 5658 | 1.76 |
BmimCl | 3458 | 5671 | 1.64 |
AmimCl | 3423 | 5579 | 1.63 |
Deposited lignin layer formed on the fiber surface by adsorption of the dissolved lignin in the cooking stage. Thus, the diffusion paths were blocked, and the development on the diffusivity and bonds of fibers were hindered.21 ILs with 1-butyl-3-methylimidazolium or 1-allyl-3-methylimidazolium cation exhibited the ability to form π–π interactions with lignin for its aromatic groups. Moreover, ILs first acted on the deposited lignin layer. After pretreatment by aqueous ILs, the surface coverage of lignin decreased substantially from 32.34% to 21.83% (BmimCl pretreatment) and 21.54% (AmimCl pretreatment). The removal of deposited lignin on the fiber surface could open more diffusion channels.
Footnote |
† Electronic supplementary information (ESI) available: Experimental and characterization details. See DOI: 10.1039/c4ra05284f |
This journal is © The Royal Society of Chemistry 2014 |